GB2118354A - Process and apparatus for the vitrification of radioactive waste solutions - Google Patents

Process and apparatus for the vitrification of radioactive waste solutions Download PDF

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Publication number
GB2118354A
GB2118354A GB08306747A GB8306747A GB2118354A GB 2118354 A GB2118354 A GB 2118354A GB 08306747 A GB08306747 A GB 08306747A GB 8306747 A GB8306747 A GB 8306747A GB 2118354 A GB2118354 A GB 2118354A
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GB
United Kingdom
Prior art keywords
liquid
feed container
offgas
vitrification
scrubbing
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
GB08306747A
Other versions
GB8306747D0 (en
GB2118354B (en
Inventor
Friedrich Kaufmann
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Deutsche Gesellschaft fuer Wiederaufarbeitung von Kernbrennstoffen mbH
Original Assignee
Deutsche Gesellschaft fuer Wiederaufarbeitung von Kernbrennstoffen mbH
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Publication date
Application filed by Deutsche Gesellschaft fuer Wiederaufarbeitung von Kernbrennstoffen mbH filed Critical Deutsche Gesellschaft fuer Wiederaufarbeitung von Kernbrennstoffen mbH
Publication of GB8306747D0 publication Critical patent/GB8306747D0/en
Publication of GB2118354A publication Critical patent/GB2118354A/en
Application granted granted Critical
Publication of GB2118354B publication Critical patent/GB2118354B/en
Expired legal-status Critical Current

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Classifications

    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/28Treating solids
    • G21F9/30Processing
    • G21F9/301Processing by fixation in stable solid media
    • G21F9/302Processing by fixation in stable solid media in an inorganic matrix
    • G21F9/305Glass or glass like matrix
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10TECHNICAL SUBJECTS COVERED BY FORMER USPC
    • Y10STECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10S422/00Chemical apparatus and process disinfecting, deodorizing, preserving, or sterilizing
    • Y10S422/903Radioactive material apparatus

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  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Physics & Mathematics (AREA)
  • Engineering & Computer Science (AREA)
  • General Engineering & Computer Science (AREA)
  • High Energy & Nuclear Physics (AREA)
  • Gas Separation By Absorption (AREA)
  • Cleaning By Liquid Or Steam (AREA)
  • Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)
  • Glass Compositions (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Description

1 GB 2 118 354 A 1
SPECIFICATION
Process and apparatus for vitrifying radioactive waste solutions Radioactive fission products produced liquid form in the first extraction cycle of a processing plant are usually vitrified since glass forms a mechanically stable product and holds the radionuclides very tightly together.
The highly radioactive fission product solution is usually fed from a storage container in measured amounts to the vitrification plant. This storage container is charged from a receiving container for the radioactive fission product solution.
The ofigases generated during the vitrification of the fission product solution in the melting furnace of a vitrification plant must be freed of the entrained dust particles and the like to prevent the potential blocking of lines and components. It is therefore customary to pass the offgas through an offgas scrubbing stage for removal of the dust particles. The offgas is scrubbed in this purification stage in counterflowwith a scrubbing solution in which the removed acids, dust particles and aerosols have accumulated.
The scrubbing liquid is conducted in a circulatory system to minimize the production of secondary radioactive waste. After a certain time, the circulat- ing scrubbing liquid is heavily contaminated and must be renewed.
It is an aim of the invention to create a process and apparatus forthe vitrification of fission product solutions, which has a simplified process cycle and in which waste scrubbing is less costly.
According to one aspect, the invention provides a process for vitrification of radioactive fission products present in liquid solution, which comprises metering the fission product solution from a feed container to a vitrifying plant and scrubbing the offgas generated during vitrification to remove entrained dust particles or the like by a scrubbing liquid in an offgas scrubber, wherein radioactive fission product solution is removed from the feed tank and fed to the head of the offgas scrubber to provide the 110 scrubbing liquid, the fission product solution is returned to the feed container after passing through the offgas scrubber, and the offgas from the vitrifying plant is conducted in counterflow through the offgas scrubber.
The process according to the invention provides for the use, as a scrubbing liquid, of the liquid fission product solution itself that is situated in the feed container. A separate scrubbing liquid, which represents additional secondary waste, is no longer necessary. The two process steps, metering of the fission product solution from the feed container and offgas scrubbing, are simplified significantly.
The offgas from the vitrification plant is preferably conducted into the feed container above the liquid level. From there, the offgas enters the offgas scrubber. This has the advantages that the offgas has already been subjected to a pre-scrubbing in the feed container before it reaches the offgas scrubber.
For the implementation of the process of the 130 invention the invention also concerns an apparatus for the vitrification of highly radioactive, liquid fission product solutions with a vitrification plant having a glass melting furnace, which is connected with a feed container for the liquid fission product solution via a metered conveyer system, and with a counterflow scrubber for scrubbing of the furnace offgas of the vitrification facility with a scrubbing liquid conducted in a circulatory system. To reduce the number of facility components, the discharge of the counterflow scrubber is connected with the feed container and a pipeline preferably provided with a metering and conveying device is arranged between the feed container and the head of the counterflow scrubber.
Thus, according to a second aspect, the invention provides apparatus for the vitrification of highly radioactive liquid fission products which comprises a vitrification plant having a glass melting furnace, a feed tankforthe liquid fission product solution connected thereto via a metering and feeding device, and a counterflow scrubber for scrubbing of the vitrification plant furnace offgas with the scrubbing liquid solution being recycled, wherein a drain outlet of the counterflow scrubber is connected to the feed container and a connection is arranged between the feed tank and the head of the counterflow scrubber.
For simplicity, the offgas scrubbing stage and the feed container for the fission product solution are preferably combined in this manner into one component.
In a preferred embodiment of the device according to the invention, the offgps line supplying the furnace offgas enters the feed container above the level of the liquid. The introduction of the offgas into the feed container is, due to structural considerations, more favourable than the introduction into offgas scrubbing column that is provided with a narrower cross-section.
In another preferred embodiment of the invention there is arranged in the feed container an air-pulse system immersed in the fission product solution. As a result of air pulses produced by this system it is possible to prevent the formation of sediments on the bottom of the feed container.
An embodiment of the invention will now be described by way of example with reference to the accompanying diagrammatic drawings.
A vitrification facility or plant 1 of generally conventional type has a glass melting furnace (not shown) which is raised to giass-melting temperature by a heater 2. The arrow 3 indicates the discharge of the molten glass with absorbed radioactive f ission products. Fritted glass is added to the vitrification plant 1 via an admixing opening (arrow 4) and the highly radioactive fission product solution is introduced in measured amounts through an inlet opening 5.
In a supply line 6 that connects the inlet opening 5 with a feed container 7, there is arranged a metering air-lift container 8 of a metering air-lift conveying device. Such air-lift conveying devices have proved themselves for the metered feed of radioactive fission product solutions. With these air-lift conveyor devices the conveying movement is brought about 2 GB 2 118 354 A 2 by bubbling air into a column of liquid. The supply of air occurs here through a line 9 at the lower end of the input line 6 arranged in the lower area of the feed container 7. The conveyance of the fission product solution by means of an air-lift is more reliable than with a pump since the air-lift has no moving parts.
This eliminates pump replacement that could poss ibly be required. No secondary waste is generated as a result of a contaminated pump and the possible exposure to radiation of the personnel during pump replacement is eliminated.
The fission product solution is supplied to the feed container 7 from a collecting tank (not shown) by pumps or by another air-lift system, via an inlet 10.

Claims (8)

The level of the liquid inside said feed container 7 is 80 CLAIMS kept between two predetermined limits at all times. Into the feed container 7 there projects a pulsation pipe 11 into which the liquid is sucked by a reduced air pressure. The pressure in pipe 11 is then raised and the liquid is forced back out of the pipe 11 into the feed container 7. The cycle is then repeated. It is the purpose of this air-pulse system to prevent sedimentation in the feed container 7. Into the feed container 7 there also projects the lower end of a scrubbing column 12 having at its head a discharge 13 forthe scrubbed furnace offgas. The scrubbing column 12 is charged in its upper region with a scrubbing liquid taken via a metering line 14, provided with an air-lift container 15, from the liquid stored in the feed container 7. The air supply for this air-lift conveyance system is provided by an input line 16. The vitrification plant 1 has an ofigas line 17 that enters the feed container 7 above the level 18 of the liquid. The feed container 7 can be cooled or heated by means of a cooling or heating element 19. The mode of operation of the apparatus described above is as follows: The fission product solution to be vitrified is 105 supplied to the feed container 7 from a collector vessel (not shown). The level 18 of the liquid in the feed container 7 is monitored so that it will be at all times between two limit values. The supply line 6 is immersed into the fission product solution and the solution is introduced in measured amounts via the input line 6 into the vitrification plant 1 by means of the metering air-lift container 8 and the supply of air via the line 9. At the same time, fritted glass (arrow 4) is charged into the vitrification plant 1. Following the 115 sintering of the fritted glass, the radioactive fission products are bonded in the glass and periodically drawn off from the vitrification plant 1. The offgas generated during vitrification entrains radioactive dust particles and enters via the offgas line 17 into the feed container 7 above the level 18 of the liquid. The offgas then traverses the sc,ubbing column 12 from the bottom up in counterflow to the scrubbing liquid charged into the upper region, which liquid has been drawn off from the fission production solution stored in the feed container 7. While passing through the scrubbing column 12, the major portion of the dust particles, aerosols, and the radionuclides volatilized during vitrification are absorbed by the amount of fission product solution serving as scrubbing liquid. The contaminated scrubbing liquid flows back into the feed container 7. On leaving the feed container 7 it is partly returned again to the head of the gas scrubber 12 and partly via the input line 6 to the vitrification plant 1. If in the fission product solution in the feed container 7 there accumulate components which, due to continuous gas scrubbing, are in excess of admissible limit values and which cannot be absorbed by the fused glass, a portion of the scrubbing solution is drawn off for additional processing. The level of the liquid in the feed container 7 is restored via the input line 10.
1. A process for vitrification of radioactive fission products present in liquid solution, which comprises metering the fission product solution from a feed container to a vitrifying plant and scrubbing the offgas generated during vitrification to remove entrained dust particles orthe like by a scrubbing liquid in an offgas scrubber, wherein radioactive fission product solution is removed from the feed tank and fed to the head of the offgas scrubber to provide the scrubbing liquid, the fission product solution is returned to the feed container after passing through the offgas scrubber, and the offgas from the vitrifying plant is conducted in counterflow through the offgas scrubber.
2. A process according to Claim 1, wherein the furnace offgas is conducted from the vitrification plant into the feed container and from there through the offgas scrubber.
3. Apparatus for the vitrification of highly radioactive liquid fission products which comprises a vitrification plant having a glass melting furnace, a feed tankfor the liquid fission product solution connected thereto via a metering and feeding device, and a counterflow scrubber for scrubbing of the vitrification plant furnace offgas with the scrubbing liquid solution being recycled, wherein a drain outlet of the counterflow scrubber is connected to the feed container and a connection is arranged between the feed tank and the head of the counterflow scrubber.
4. Apparatus according to claim 3, wherein the connection is a pipeline with a metering-conveying device.
5. Apparatus according to claim 3 or 4, wherein an offgas line supplying the furnace offgas to the feed container enters above the level of the liquid.
6. Apparatus according to Claim 3,4or5, wherein an air-pulse system is arranged in the feed container and is immersed in the fission product solution.
7. A process for vitrification of radioactive fission products present in liquid solution, substantially as hereinbefore described with reference to the drawing.
0 4_ 1 A i 3 GB 2 118 354 A 3
8. Apparatus for the vitrification of highly radioactive liquid fission products, substantially as hereinbefore described with reference to the drawing.
Printed for Her Majesty's Stationery Office, by Croydon Printing Company Limited, Croydon, Surrey, 1983. Published by The Patent Office, 25 Southampton Buildings, London, WC2A lAY, from which copies may be obtained.
GB08306747A 1982-03-13 1983-03-11 Process and apparatus for the vitrification of radioactive waste solutions Expired GB2118354B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
DE3209250A DE3209250C2 (en) 1982-03-13 1982-03-13 Method and device for cleaning the furnace exhaust gas from a glazing plant

Publications (3)

Publication Number Publication Date
GB8306747D0 GB8306747D0 (en) 1983-04-20
GB2118354A true GB2118354A (en) 1983-10-26
GB2118354B GB2118354B (en) 1985-07-31

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GB08306747A Expired GB2118354B (en) 1982-03-13 1983-03-11 Process and apparatus for the vitrification of radioactive waste solutions

Country Status (7)

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US (2) US4592898A (en)
JP (1) JPS58168997A (en)
BE (1) BE896046A (en)
BR (1) BR8301242A (en)
DE (1) DE3209250C2 (en)
FR (1) FR2523360B1 (en)
GB (1) GB2118354B (en)

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JPS6036999A (en) * 1983-08-09 1985-02-26 株式会社荏原製作所 Volume-reduction solidified body of radioactive sodium borate waste liquor, volume-reduction solidifying method anddevice thereof
US4908315A (en) * 1987-03-04 1990-03-13 Agristar, Inc. Integument and method for micropropagation and tissue culturing
US4762991A (en) * 1987-05-29 1988-08-09 Battelle Memorial Institute Probe for optically monitoring progress of in-situ vitrification of soil
US4898692A (en) * 1988-11-16 1990-02-06 The United States Of America As Represented By The United States Department Of Energy Process for direct conversion of reactive metals to glass
US5405590A (en) * 1993-02-05 1995-04-11 Pedro Buarque de Macedo Off-gas scrubber system
US5326532A (en) * 1993-02-25 1994-07-05 E. I. Du Pont De Nemours And Company Apparatus for chemically processing toxic materials
US5711635A (en) * 1994-05-20 1998-01-27 Stir-Melter, Inc. Apparatus for hazardous waste vitrification
US5536114A (en) * 1994-05-20 1996-07-16 Stir-Melter, Inc. Apparatus for vitrifcation of hazardous waste
US5678237A (en) * 1996-06-24 1997-10-14 Associated Universities, Inc. In-situ vitrification of waste materials
RU2115182C1 (en) * 1997-09-09 1998-07-10 Московское государственное предприятие Объединенный эколого-технологический и научно-исследовательский центр по обезвреживанию РАО и охране окружающей среды Device for vitrifying radioactive wastes containing ion- exchange resins

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GB1031884A (en) * 1962-04-06 1966-06-02 Commissariat Energie Atomique Process and apparatus for the concentration of dangerous solutions
GB1063533A (en) * 1964-04-03 1967-03-30 Aqua Chem Inc Concentration of solutions containing radioactive materials by evaporation
GB1163099A (en) * 1966-02-18 1969-09-04 Euratom Process and Apparatus for the Combustion and Evaporation of Radioactive Residues.
GB1421654A (en) * 1972-02-02 1976-01-21 Boehler & Co Ag Geb Method and apparatus for vaporizing liquids
GB1482780A (en) * 1974-07-22 1977-08-17 Aerojet General Co Radioactive waste disposal process

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GB1031884A (en) * 1962-04-06 1966-06-02 Commissariat Energie Atomique Process and apparatus for the concentration of dangerous solutions
GB1063533A (en) * 1964-04-03 1967-03-30 Aqua Chem Inc Concentration of solutions containing radioactive materials by evaporation
GB1163099A (en) * 1966-02-18 1969-09-04 Euratom Process and Apparatus for the Combustion and Evaporation of Radioactive Residues.
GB1421654A (en) * 1972-02-02 1976-01-21 Boehler & Co Ag Geb Method and apparatus for vaporizing liquids
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Also Published As

Publication number Publication date
BR8301242A (en) 1983-11-22
GB8306747D0 (en) 1983-04-20
US4615833A (en) 1986-10-07
FR2523360B1 (en) 1987-11-06
US4592898A (en) 1986-06-03
JPH0246118B2 (en) 1990-10-12
DE3209250C2 (en) 1986-01-23
BE896046A (en) 1983-06-16
GB2118354B (en) 1985-07-31
DE3209250A1 (en) 1983-09-22
FR2523360A1 (en) 1983-09-16
JPS58168997A (en) 1983-10-05

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PCNP Patent ceased through non-payment of renewal fee

Effective date: 19940311